Short Term Monitoring Program South Dingley Village, VIC
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1 Short Term Monitoring Program
2 Version Control Page Summary Version 2: 11 May and 5 Update of dot point 8 (page 4) regarding contribution of community noise on captured events. Deletion of Table 1 (page 5) and addition of dot point 9 (page 4). Glossary of Terms A Arrivals Background noise level (L90) The sound level in db(a) that is exceeded 90% of the time Correlated Noise Event (CNE) A noise event correlated to an aircraft operation that flew through the capture zone Correlation Summary Percentage of captured aircraft operations correlated with noise events recorded by the noise monitor D Departures Day 6:00am to 11:00pm EMU Environmental Monitoring Unit H Helicopters LAmax Maximum sound level in db(a) Local Operation that departs and arrives at the same airport. Local movements include circuits and training flights. Movement An aircraft operation, such as an arrival or departure Night 11:00 pm to 6:00 am NFPMS Noise and Flight Path Monitoring System Noise Event A noise that exceeds the threshold sound level for longer than the threshold time that is set O Overflight i.e. an aircraft movement that flew over the area but did not arrive or depart from the airport of concern T Local Operation (Departure and Arrival) Threshold Pre-set level on noise monitor that triggers a noise event when exceeded For further information on the metrics used in this report refer to Australian Standard Acoustics Description and measurement of environmental noise. Airservices Noise Monitoring Program Information about Airservices noise monitoring program is available on the Airservices website, including reports of the noise and operational data collected by the Noise and Flight Path Monitoring System, as well as fact sheets about topics related to aircraft noise. The website is available at: Contact Us To lodge a complaint or make an enquiry about aircraft operations, you can go to WebTrak ( use our online form ( telephone (freecall) or (local call Sydney) fax (02) or write to, Noise Complaints and Information Service, PO Box 211, Mascot ACT Airservices Australia. All Rights Reserved. This report contains a summary of data collected over the specified period and is intended to convey the best information available from the NFPMS at the time. The system databases are to some extent dependent upon external sources and errors may occur. All care is taken in preparation of the report but its complete accuracy can not be guaranteed. Airservices Australia does not accept any legal liability for any losses arising from reliance upon data in this report which may be found to be inaccurate. Version 2: 11 May 2015 Page 2 of 5
3 Deployment Purpose Short term noise monitoring was conducted at South Dingley Village following recommendations made by the community. The purpose of this report is to provide a technical summary of the recorded aircraft noise and operational data collected at South Dingley Village during October 2014 to January An explanation of terms used within this report can be found in the Glossary on page 2 of the report. Deployment Monitoring Period 21/10/14 12:00 am 20/01/ :00 am Environmental Monitoring Unit (EMU) Details Location St Mark s Primary School, Dingley Village VIC 3172 Latitude 37 59' 10.96"S Longitude 145 7' 43.87"E NMT Altitude 82 ft above mean sea level Capture Zone 2.5 km radius with 8,000 ft (above ground level) height for noise data capture Threshold Settings 50.0 db(a) to 55.0 db(a) depending on time of day Moorabbin Airport Noise and Flight Path Monitoring System Improvement Program (NFPMS) Aircraft movements from Moorabbin Airport have been visible in the Melbourne component of Airservices Noise and Flight Path Monitoring System (NFPMS) for many years. For example flight tracks in and out of Moorabbin Airport can be seen in WebTrak. The NFPMS was originally setup to monitor operations at major airports and relied upon obtaining the details of the operations from a lodged flight plan. Moorabbin Airport is a General Aviation airport with a high proportion of operations relating to training schools. As a result, the majority of movements at Moorabbin Airport do not have a detailed flight plan and therefore there is limited data captured by the NFPMS. Recently Airservices has developed new capability within the NFPMS to determine movement details in the absence of lodged flight plans at Moorabbin. This improved capability has been trialled since October 2014 and the short term monitoring included in this document has benefitted from the improved NFPMS at Moorabbin. Version 2: 11 May 2015 Page 3 of 5
4 South Dingley Village Findings The noise monitor was located in Dingley Village 3 km to the east of Moorabbin airport. 20,678 movements flew through the capture zone during the reporting period. 20,052 of these were Moorabbin operations. 46% of total operations that flew through the capture zone (as shown in figure 2) were local touch and go operations, including circuits, from Runway 17L. There were a total of 9,682 correlated noise events above 60 db(a). These were most common during the weekday and weekend hours of 10:00 am, 11:am and 3:00 pm. 35 correlated noise events over 60 db(a) occurred during the hours of night (11:00 pm to 6:00 am). The number of correlated noise events exceeding 60 db(a) in any one day ranged from one to 222, with an average of 111 events daily. 132 noise events over 75 db(a) were recorded during the reporting period. This occurred four times during the hours of night (11:00 pm to 6:00 am). The vast majority of operations at Moorabbin Airport are general aviation (GA) aircraft. The most common, during the period reviewed, being the Piper Cherokee Warrior (PA ). There are also a few arrivals and departures of regular passenger transport. A breakdown for common general aviation aircraft types is given in Table 2 and 3. The loudest correlated aircraft noise event with a max level of 80.7 db(a) was a propeller departing from Runway 17L. Correlated events as high as db(a) were recorded during the reporting period however upon review of a sample of recorded noise events, it was identified that community noise contributed to an extent not anticipated at this site. Community activities including construction, mowing and traffic can cause such events to be recorded on the monitor. At this site, community noise cannot readily be separated from aircraft noise events. A proportion of correlated noise events captured at this monitor would not accurately reflect the true aircraft noise. The average LAmax for this monitor was 63.5 db(a). The correlation summary for all movements was 55%. This is considered an improvement on similar studies conducted at secondary airports. For more information please refer to Figure 1, Figure 2 and Tables 1-2 on page 5. Version 2: 11 May 2015 Page 4 of 5
5 FIGURE 2: OPERATIONS THAT TRAVERSED DINGLEY VILLAGE ON 10/12/2014 TABLE 1: TOP 4 AIRCRAFT TYPE RECORDED AT MOORABBIN AIRPORT, 3 9 NOVEMBER 2014 Aircraft Type Airport Arrivals Departure Touch & Go All Movements PA Moorabbin 14% 14% 31% 22% 172S Moorabbin 10% 9% 15% 12% 152 Moorabbin 3% 3% 13% 8% Light Sports Aircraft Moorabbin 6% 6% 9% 7% Total Movements Moorabbin (3/11/14 9/11/14) TABLE 2: TOP 4 HELICOPTER TYPE RECORDED AT MOORABBIN AIRPORT, 3 9 NOVEMBER 2014 FIGURE 1: DINGLEY VILLAGE NOISE SUMMARY 21/10/ :00AM 20/01/ :00AM Aircraft Type Airport All Helicopter Movements 269C 1 Moorabbin 21% R44 II Moorabbin 16% 206B Moorabbin 12% AS.350BA Moorabbin 10% Total Helicopter Movements (3/11/14 9/11/14) Moorabbin 228 Version 2: 11 May 2015 Page 5 of 5
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